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doi: http:// dx.doi.org/10.15446/v64n3sup.50550 e-ISSN 2323-0118
Participatory breeding: tool for conservation of neglected and underutilized crops Mejoramiento participativo: herramienta para la conservación de cultivos subutilizados y olvidados
Creucí Maria Caetano1*, Richard Danilo Peña C.1, José Luis Maigual J.1,2, Linda Nataly Vásquez D.1, Diego Caetano Nunes1, Bruna Rafaela C.N. Pazdiora1,2
1GIRFIN – Research Group on Neotropical Plant Genetic Resources, Universidad Nacional de Colombia - Palmira, Valle del Cauca,
Colombia. 2Universidade Federal de Rondônia, campus Presidente Médici, Brasil.
*Corresponding author: [email protected]
Abstract
Although a significant number of plant species are recognized as food, only a small fraction meets the protein
demand of the world population. Breeding crops, with a very narrow genetic base, most likely will not counteract the adverse effects of climate change. On the contrary, the crops named as underutilized, neglected, orphaned, obsolete or minor, may contain the answers in their genomes to ensure safety, nutrition and food sovereignty of populations. Duly adapted to extreme growing conditions, these local varieties, such as indigenous and landraces of Colombian maize, are part of the cultural heritage of many ethnic groups or native people, that select, use and conserve these varieties. Besides these, another concept refers to the promising resources, also little used, although for different reasons. Therefore, Participatory Plant Breeding is a tool to promote traditional local varieties or underutilized crops, to meet the needs of communities. In the PPB, members of the production chain (farmers, breeders, technicians and others) work together in the process of development of varieties, in a decentralized and participatory process. A PB program with Colombian maize germplasm resulted in the promotion of some local varieties. Alongside, new maize landraces to Colombia were described.
Key words: Orphaned crops, underutilized species, original peoples, race, ancestral knowledge, local variety.
Resumen
A pesar de un número significativo de especies vegetales ser reconocidas como alimenticias, solo una pequeña
fracción cumple con la demanda proteica de la población mundial. Los cultivos mejorados, con una base genética muy limitada, muy posiblemente no podrán contrarrestar los efectos adversos del cambio climático. Por lo contrario, los cultivos considerados subutilizados, infrautilizados, olvidados, huérfanos, obsoletos o menores, pueden contener en sus genomas las respuestas para garantizar la seguridad y la soberanía alimentaria y nutricional de las poblaciones. Esas variedades locales, debidamente adaptadas a condiciones agroclimáticas extremas, como las de maíz criollo e indígena colombiano, hacen parte del patrimonio cultural
de muchos grupos étnicos o pueblos originarios, que las seleccionan, las utilizan y las conservan. Además de estos, otro concepto se refiere a los recursos promisorios, igualmente poco utilizados, aunque por razones diferentes. Así, el Mejoramiento Participativo es una herramienta para promocionar variedades locales o cultivos tradicionales subutilizados, por atender las necesidades de las comunidades. En el Fitomejoramiento Participativo, los miembros de la cadena de valores o productiva (agricultores, fitomejoradores, técnicos y otros) trabajan juntos en el proceso de desarrollo de las variedades, en un proceso descentralizado y participativo. Un programa de MP con germoplasma de maíz colombiano resultó en la promoción de algunas variedades locales. Paralelamente se describieron nuevas razas de maíz para Colombia.
Palabras clave: Cultivos huérfanos, especies subutilizadas, pueblos originarios, raza, saber ancestral, variedad local.
Plant Breeding and Plant Genetic Resources / Mejoramiento Genético Vegetal y Recursos Fitogenéticos
Participatory breeding: tool for conservation of
neglected and underutilized crops
384
Introduction
Genetic resources (GR) and their surroundings at global level, are found, according to the
IUCN - International Union for Conservation of Nature (Buyck et al., 2015) – and the FAO -
Food and Agriculture Organization of the Uni-
ted Nations (2015), under imminent risky situ-
ations of several origins, from natural causes till the depredatory human intervention on the
environment (WCMC, 1992).
The most recent situation, climate change,
anticipates an uncertainty state about how to
feed the world population and ensure the avai-
lability of the domesticated species by the di-fferent human groups since the onset of agri-
culture. It is foreseen that for 2050 the human
population will be 9000 millions of people
(FAO, 2015), distributed mainly in marginal
zones, that present high levels of food and nu-trition insecurity. In this sense, the survival of
the human race is in his own hands.
According to FAO (2015), there are more
than 500 million of family units habiting the
agricultural areas of the planet which produce
most of their food. However, although diverse, thee cities are placed on the extremely poor
strings with low productivity levels. In order to
promote a sustainable growth of productivity,
strategies for improving harvesting yields, ge-
netic resources conservation and adoption of innovative management practices for crops
should be applied, generating aggregate value
and increasing the rural income.
In many of these marginal areas, in addi-
tion to conventional crops, domesticated or
semi-domesticated germplasm, product of tar-geted selection and maintained by indigenous
peoples and other traditional communities,
with broad genetic base, adapted to abiotic
stresses such as adverse weather and ecologic
conditions, or biotic, as tolerance or resistance to pests and pathogens.
Founded in 2004, the Research Group on
Neotropical Plant Genetic Resources (GIRFIN)
of the Universidad Nacional de Colombia –
Palmira, supports the postgraduate programs
in the Faculty of Agricultural Sciences, in spe-cial the Master in Biological Sciences with fo-
cus on research on Neotropical Plant Genetic
Resources. In its academic, extension and re-
search actions, it has built special human ca-
pabilities to work on topics that contribute to
characterize, preserve, value, document, ma-
nage and use sustainably plant genetic re-
sources.
According with this perspective, the GIRFIN, develops basic and applied studies
with different GR, mostly on Andean crops and
from the Andean valleys and wild relatives of
cultured species. Used tools are Participatory
Action Research –PAR, in special the Participa-tive Plant Breeding (PPB). Colombian local ra-
ces and varieties of maize are considered as
those crops that, although with broad genetic
base, have been minimally or poorly used.
PPB is understood as a decentralized and
participatory form of improvement where the community members, plant breeders and tech-
nicians actively participate to obtain certain
germplasm that meets the needs and prefe-
rences of farmers and indigenous peoples, es-
pecially in marginal areas (Ashby, 2009). The communities are those who, in principle, decide
what they want and what they want to improve,
thereby contributing to its food and nutrition
security and sovereignty.
The two basic and more recognized strate-
gies for PPB, used for the first time in the nine-ties in Syria, Morocco and Tunes, according to
Cecarelli (2012), are PVS (Participatory Evalua-
tion and Selection of fixed lines or varieties;
Participatory Varietal Selection) and PPB itself
(participatory creation and selection in segre-gant populations, Participatory Plant Breeding
PPB).
In the PVS, the objective is to value the
available germplasm. Easy to implement and
with own cost, at short term it generates re-
sults, it means, the varieties are rapidly adop-ted by the participant farmers of the process.
For decision making the appreciation from the
farmers and the agronomical results are com-
plemented.
In turn, the PPB is applied when the objec-tive is to rescue and/or value the quality of the
local varieties, or for marginal environments
and/or specific crop conditions or quality re-
quests, or to increase the genetic base, or when
the PVS did not reach satisfactory results.
Therefore, it involves aspects associated to the following set goals:
1 To recognize the PB as a tool that supplies
food and nutritional security and sovereign-
ty to the local communities of Colombia,
contributing to the preservation and promo-
tion of the forgotten, underutilized, orphan,
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
385
outdated and minor PGR, together with
having the potential to counteract the ad-
verse effects of climate change;
2 To promote PB techniques in farmer, indi-
genous and academic communities, as an
alternative to promote and use germplasm,
and as consequence, to preserve it.
Plant genetic resources
According to the UPOV (1991), CBD (1992),
FAO (1996) and the World Conservation Moni-
toring Centre (WCMC, 1992) a plant genetic
resource is “the material of reproduction or vegetative propagation of the following types of
plants:
1 Crop varieties (cultivars) currently in use
and newly obtained varieties;
2 Disused cultivars (obsolete);
3 Primitive cultivars (local varieties);
4 Wild and weed species (currently con-
sidered as weeds or companying plants),
close relatives to crop varieties;
5 Special genetic lines.
Associated to these crop species are found the wild relatives, important sources of genes
with immediate use in plant breeding pro-
grams. However, those wild relatives and the
ancestral crops have been neglected without
recognizing their value for use and/or disuse.
Traditional crops are identified in several categories according to their frequency of use,
exploitation and position in the market: forgo-
tten, underutilized, orphan, outdated and mi-
nor plant genetic resources. These PGR are
somehow accepted by the ITPGRFA and GPA
(FAO, 1996, 2011). Besides them, another ca-tegory of underutilized PGR belongs to the
promising crops which have food and/or agri-
cultural potential that has not been properly
recognized.
Plant genetic resources for food and
agriculture (PGRFA) and the global plan of action (GPA)
Through the International Treaty on Plant Ge-
netic Resources for Food and Agriculture –
ITPGRFA, FAO (1996) have determined some regulations with the common objective of pre-
serving and make a sustainable use of the
PGR, associated to a set of activities that
assume the startup of those strategies dis-
played by the Global Plan of Action (GPA), in its 1996 and 2011 versions.
Defined by a group of priority actions, the
GPA should offer answers to the use and
preservation of plant genetic resources for food
and agriculture, among their different catego-ries, that ensure to the communities the safety
and sovereignty in their food and nutrition,
coupled to sustainable agriculture and sus-
tainable management of ecosystemic resources
(FAO, 2011c). This means that it is priority, not
only the production, but the availability and access to food resources on a fair and even
manner, for the current or future use, accor-
ding to the international regulations and
agreements intended to this matters.
As basic principle and in summary, the ITPGRFA and the GPA have as common goal
the preservation of PGRFA and the promotion
of local varieties, that have genetic value (op-
tion) and quasi option (information), with po-
ssible potential to confront climate change. In
general, after its revision in 2011, the GPA ob-jectives are
1 To promote effectiveness and efficiency in
the global actions for preservation and sus-
tainable use of PGRFA;
2 To link the preservation with the use in order to better use the plant germplasm;
3 To strengthen the systems for seeds and
crop breeding as an impulse for economic
development;
4 To create capabilities, strengthen the na-
tional programs and widen the collabora-tions for PGRFA management;
5 To consolidate the implementation of the
International Treaty for Plant Genetic Re-
sources for Food and Agriculture.
A first step in knowing and recognizing the PGR of a country or region for their value and
sustainable use, is the generation of species
inventories. These can be done using basic
tools as collection and taxonomic identification
activities, till the use of more sophisticated
technologies like bioprospection, that uses geo-graphic information systems (GIS) and other
tools to diagnose and monitor the biological
diversity of each country for preservation and
valuation.
Participatory breeding: tool for conservation of
neglected and underutilized crops
386
Concepts of biodiversity and agrobiodiversity
Biological diversity or biodiversity (BD) is the
variety of life in the planet Earth including the
resources comprising the genetic heritage, re-presented by the different plant, animal and
microorganism species, all the genetic variabi-
lity among species and all the diversity in the
ecosystems composed of different combinations
of species (CDB, 1992). Biodiversity also refers to the complex relationships among live beings
and between them and their environment
(BRASIL, 2008).
Additionally the BD comprises the envi-
ronmental goods and services –food, drugs,
clean water and air and, other natural re-sources that sustain several human activities-.
To keep the biodiversity in front of the growing
human impact is one of the biggest challenges
nowadays (Toledo Machado, Santilli, and
Magalhães, 2008).
The GIRFIN considers the biodiversity from
a wide and holistic meaning. Thus, the biodi-
versity is the product of the summation of all
the resources of flora, fauna and microorga-
nisms which are affected by anthropic action,
where the ancestral crops are highlighted by their management and use, associated to the
traditional and ancestral knowledge. Therefore,
there are three supplementary views of biodi-
versity: biologic, ethnic and cultural, that con-
tinuously interact.
In the fifth meeting, in 2000, in Nairobi,
Kenya, the COP-5 adopted decisions on a wor-
king program on arid and sub-humid lands;
ecosystemic approaches; access to genetic re-
sources; exotic species; sustainable use; biodi-
versity and tourism; incentive measures; Global Strategy for Plant Preservation; Global Taxo-
nomy Initiative (GTI); CHM, financial resources
and mechanisms; identification, monitoring,
evaluation and indicators; evaluation of im-
pacts, responsibility and compensation; and finally, the definition of the term Agrobiodiver-
sity, which established a link between this and
the preservation role of the ancestral communi-
ties. COP-5 also included a high level segment
on the Cartagena Protocol on Biosafety with a
Ministries Roundtable and a Special Signature Ceremony (Toledo Machado, Santilli and
Magalhães, 2008).
Preservation of crops or forgotten and underutilized species (EOS/NUS)
Although the PGR are considered to be 300.000
identified species and 30.000 are catalogued as
edible plant species, only three crops – maize, wheat and rice- represent around 40 to 50% of
the global calorie and protein consumption
required in the food diet and, only 30 supply
95% of the food global needs (Thies, 2000; EM-
BRAPA, 2015).
Several crops that have been used histori-
cally for food and other uses at a larger scale,
or, that can be used because their potential,
have been neglected to the underutilized, or-
phan, obsolete and/or minor state. As a whole,
these marginal crops are known as NUS (Padu-losi et al., 2011). To these traditional underva-
lued crops Silva-Ramos (2002) name them, in
general, as marginal crops, even though they
are extremely important in food and nutritional
security and sovereignty in the Andean region
and have an almost unlimited genetic breeding potential.
Hernandez-Bermejo & León (2013) consider
as marginal species those crops that in the
past and in the current conditions were repre-
sentative for the agricultural activity or the traditional agriculture and, also, in the feeding
of indigenous ethnic groups and other local
communities. They are not promising crops
since they were cultured in a more recent past.
However, currently they do not represent areas
in production or substantial consumption. Their distribution relies on regulations and
dissemination strategies and, their rescue do
not require their intensive production nor their
use as product for exportation only.
Such crops are characterized by:
1 Being local and traditional, and their distri-
bution, biology, cropping and use are badly
documented;
2 Being linked to the cultural heritage of their
location of origin;
3 Being adapted to specific agroecological niches and marginal lands;
4 Participating on an informal or formal sys-
tems (in some cases) for seed supply (small
scale);
5 Being present in traditional agroecosystems for production, with low or none external
input;
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
387
6 Having traditional uses in localized areas;
7 Receiving low attention by research, ex-
tension services, decision makers, donors, technology providers and consumers, de-
spite their potential for diet diversification
and supply of micronutrients like vitamins
and minerals;
8 Being very nutritive and/or with medicinal properties and other multiple uses, like en-
vironmental services because of their adap-
tation to marginal soils or weather condi-
tions;
9 Playing an important role in the sub-
sistence or survival and in the economy of marginal regions in the planet, especially in
the tropics, where the agrobiodiversity is rich (Pastor et al., 2007).
According to Hernández-Bermejo & León
(2013), the reasons why a crop or species be-
comes marginal are social, agronomic and bio-logic, predominating the first ones. Among the
reasons are the substitution of local germplasm
by a more productive one; disappearance of
ethnic groups that knew the techniques and
uses of the species, additional to the crop ma-nagement; demand variation; restrictions at the
economic, cultural, politic or religious levels,
leading to the deliberate eradication of self-
sufficient life forms, that are replaced depen-
ding on outside interests.
Categories for NUS
Underutilized and forgotten species (NUS) are
important resources for agricultural and rural
development, because they positively con-tribute to life wellness through better incomes
and nutrition, additionally they include cultu-
ral dimensions associated with history, religion
and mores of the communities (GFU, 2007).
Different concepts have been stated to de-
fine what are and which the categories are for NUS. Thus, according to some authors, is in-
cluded:
1 FAO/WHO (1992): “a marginal crop is one
that in the past, under different conditions,
was more important in conventional agri-culture, but now it focuses on feeding of lo-
cal communities and allowing food sustai-
nability of the populations with subsistence
economy”;
2 IPGRI (1998) currently Biodiversity Interna-
tional: “…crops (which) may become widely
distributed, but tends to occupy restricted
niches in the economy and local production; they are maintained by soci-
ocultural preferences and practices of local
use”;
3 Thies (2000): “species of these crops are
inadequately characterized and margi-nalized by research and conservation pro-
grams”;
4 Padulosi & Hoeschle-Zeledon (2004): “the
main characteristics of underutilized spe-
cies are its great importance in local pro-
duction systems and self-consumption; great adaptability to different agro-
ecological niches and marginal areas; being
excluded from research and development
agendas and national policies; cultivation
and use are developed based on local and traditional knowledge; the need, in most ca-
ses, of a significant degree of genetic bree-
ding and management; the fragility and
even lack of seed supply systems and low
representation in national gene banks.”
5 GFU (2004): “an underutilized species is one whose potential is not fully utilized or
exploited to contribute to food security and
poverty reduction”;
Other concepts and terms that identify
these crops are:
1 Underutilized or forgotten crop: SUB-O – is
“that crop grown in restricted areas, with
small production, local presence (not in
large national or international markets) and
very sporadic. It may have been used for
centuries or millennia for human food, fi-ber, forage, oil or medicinal properties, but
have declined in importance over time”;
2 Orphan crop: HUÉR – refers to “that crop
specially found in marginal regions, without
any research, therefore, there is insufficient information” (value of quasi option);
3 Obsolete crop: OBSO – is “that crop/
commercial variety previously sowed but,
currently with less use and outside the
market.”
Other terms that are strictly associated are:
4 Promising crop: PROM –“that crop with
great potential for use, but that has not
been exploited enough and still has low
production and sowing area; often it is not
defined its management”. According to this
Participatory breeding: tool for conservation of
neglected and underutilized crops
388
feature, it can also refer to an orphan crop.
5 Native or indigenous crop: NATI –“species in
its center of origin or domestication (where its wild relatives are found)”;
6 Introduced crop: INTR –“introduced species
(exotic), with good adaptability, sometimes
renaturing”;
7 Domesticated crop: DOME –“species that depends on for survival (reproduction) on
anthropic actions”;
8 Semi-domesticated crop: SEM-D –“species
in process of domestication”;
9 Wild relative: PSPC/PSEC –“wild relative of
plants/cultured species”;
10 Race: – “a group of individuals with enough
number of common characters to be recog-
nized as a group” (Anderson & Cutler
1942);
11 Creole race: RC –“genetic material intro-duced several years ago, that has been se-
lected and adapted according to some envi-
ronmental conditions”;
12 Indigenous race: RI –“genetic material se-
lected and preserved by native peoples un-
der some specific environmental condi-tions”;
13 Local variety: VL –“genotype with some
characteristics that secure its use, although
with low production and, which diffusion is
done through informal seed markets, seed fairs, exchanges and other interchange
forms”.
The concept of variety
The International Union for the Protection of New Varieties of Plants (UPOV, 1991) defines
“variety” as a group of plants within a single
botanical taxon of the lowest known rank that,
with interdependence of itself, do or do not fully
respond to the conditions for the grant of a breeder's right, which can:
1 Be defined by the expression of the resul-
ting characters of a genotype or a combina-
tion of genotypes;
2 Be recognized from any group of plants by
the expression of at least one of such cha-racters;
3 Be considered as a unit, because its apti-
tude to propagate without alteration.
Toledo Machado, Santilli, and Magalhães,
2008 consider local and/or traditional varieties
as the basis of family and native people’s agri-culture as result of the management and gene-
tic selection for adaptation to different envi-
ronments, translating into an essential cultural
heritage of humanity, which will ensure food
and nutrition security and sovereignty.
Frankel and Brown (1984), Thurston et al.
(1999) and Toledo Machado, Santilli, and
Magalhães, 2008 define as traditional variety a
race or a variable population of cultured plants,
adapted by the farmer using the natural condi-
tions or artificial selection. They are adapted to the management system from the adopted crop
and/or developed by local communities, collec-
tively, according to their relationship with the
environment and also, are being cultivated in
the same agroecosystem for at least three su-
ccessive generations.
According to Toledo Machado, Santilli, and
Magalhães, 2008 by old traditional variety is
understood a meaning that is the same as the
previous one, but that was developed in the
primary and secondary centers of origin, se-lected by more than ten family generations. In
contrast, a local variety is a population under
continuous management in at least five cycles
of crop by farmers in specific agro-ecological
and socio-economic environments. In turn, Thurston et al. (1999) define a modern variety
as that selected by improved or 'scientific'
methods, for agronomic characteristics, among
others, such as production, plant height,
response to inputs. Finally, the term native
variety is used for both a traditional variety to a
local variety introduced in a community for less than 20 years (Toledo Machado, Santilli, and
Magalhães, 2008).
Marginal crops in some countries of South America and Spain
Some crops in the different categories for
marginality are described as follows for diffe-rent countries or regions.
Andean region
Silva-Ramos (2002) showed a list of native
Andean species but, many of them are subjec-
ted or vulnerable to genetic erosion processes, they need attention by the responsible entities
for preservation, among them:
1 Andean roots and tubers: oca (Oxalis spp.),
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
389
potato (Solanum spp.), camote (Ipomoea
spp.), mashwa (Tropaeolum spp.), arracacha
(Arracacia spp.), ajipa (Pachyrrhizus spp.);
2 Grains: quinoa (Chenopodium spp.);
quiwicha (Amaranthus spp.), tarwi or chocho (Lupinus spp.);
3 Fruits and vegetables: cocoa (Theobroma
spp.), sinini (Annona spp.), tuna (Opuntia
spp.), paico (Chenopodium spp.); chilto
(Physalis spp.), motacú (Attalea pharelata),
pacay (Inga spp.), guayaba (Psidium spp.),
achachairú (Rheedia spp.) and peanut (Ara-chis spp.);
4 Stimulants and spices: different kinds of pepper (Capsicum spp.).
And more: Phaseolus spp., Manihot spp.,
Lycopersicon spp., Mirabilis spp., Cucurbita
spp., Carica spp. (posibly Vasconcellea spp.)
and Passiflora spp.
Ecuador
Espinosa et al. (1996) surprisingly state as
marginal crops in the Ecuadorian territory the ARTCs (Andean roots and tubers), mainly the Arracacia xanthorhiza (white carrot), Ullucus tuberosum (ollucos), Oxalis tuberosa (oca), Tro-paeolum tuberosum (mashua) and Canna edulis
(achira). Their cropping has reduced drastically
in 10 to 20 years.
However, in this case the interest for their use has not been reduced, but some factors are
shown as limiting for the sowing of ARTCs,
among them, the unavailability of seeds, ad-
verse weather conditions (frost, wind), the soil
fertility reduction, irrigation inaccessibility,
high cost of agricultural inputs and pests that affect these crops.
Bolivia
According to Silva-Ramos (2002), the highest
value for the genetic resources in Bolivia, pri-
mary center of origin of several plant species, consists on the high inter and intraspecific
genetic variability and also in its cultivars.
These comprise the genetic material of high
importance to be used at the short, middle and
long term in breeding programs, either conven-
tional, assisted or by Participative Breeding (PBP). A PBP program can be developed in qui-
noa, beans, sweet potatoes, corn, peanuts, ca-
ssava, potato, squash and peppers, among
others.
Taking into account the active centers for
germplasm conservation, the ex situ method for
those species of orthodox seeds in Bolivia. For
recalcitrant seeds the recommended preserva-tion is in situ till in vitro conservation is imple-
mented at the centers. Agroforestry species,
pastures and others must specifically involve conservation in situ, under the system of pro-
tected areas and/or agro-ecological systems
(Silva-Ramos, 2002).
Peru
Pastor et al. (2007), point out as main un-
derutilized crops in Peru to “those native crops
that meet at least, two of three proposed crite-
ria, (1) low production, (2) irregular presence or
absence in the exports market and (3) absence
in the capital city´s markets. Among the un-derutilized crops in Peru are some ARTCs like
potatoes, ollucos, oca, mashua, tomatoes,
sweet potato, Andean cereals and grains ((qui-
noa, amaranto, some maize varieties) and
fruits.
Brazil
Bohrer-Monteiro Siqueira and Veasey (2009),
name the role of traditional agriculture that,
besides directly generate diversity, keeps ‘ethno
varieties’ of cassava, yams and sweet potato, all
with high genetic variability. If human action does not exert direct influence, these local vari-
eties resist in nature for a short time or become
extinct due to competition with wild plants.
This aspect differentiates domesticated plants -
crop- from wild plants and demonstrates the interaction of dependence to crop plants –
human being-.
According to the same authors, a diagnosis
of the causes of abandonment or loss of these
local depreciated or in marginal state varieties,
initiated through a reading of rural areas, and especially the socio-economic and environmen-
tal situation in which family farming is inser-
ted, leading to strategies for rescue and wider
use of ethno varieties of cassava, yams and
sweet potatoes.
Spain
Hernández-Bermejo and León (1992), draw
attention to forgotten crops and uses in Spain.
The marginalization of many crops is the "re-
sult of the impact of the flora of the Old World
in America and American flora in Spain. Among these causes:
a. Loss of competitiveness of some species in
front of more productive ones;
Participatory breeding: tool for conservation of
neglected and underutilized crops
390
b. Slow and progressive changes in the mores,
feeding habits and life styles;
c. Stablished competence by the economic and politic interests outside the reference
region and cultures;
d. Religious or cultural persecutions generally
associated to the previous cause;
e. Disappearance of ethnic groups and local communities that know the uses of the
plants and crop forms and uses”.
However, Hernández-Bermejo (2013), high-
lights that “the Iberian agrodiversity also su-
ffered in parallel a significant loss with margi-
nalization or neglect of many crops altogether”. Some were hidden, others came and settled in
the "New Continent, being conserved until to-
day, incorporated into its ethnobotanical, agri-
cultural and food heritage.”
“Hence the Maya gardens are (…) a (…) niche for in situ conservation of NUS, especially
of some subtropical fruits like citrus and, (…) in the feeding of some countries like Argentina
it is preserved the consumption of bitter herbs
like arugula and radicchio”, being possible “to
recuperate the germplasm (…) including their
associated food traditions”. Hernández-Bermejo
(2013) concludes that crop diversification by using NUS, will always be a successful strategy
and overall a need for agriculture.
Colombia
Caetano and coworkers have proposed, from
direct and indirect inventories, the construc-tion of a NUS list for Colombia, with emphasis
on those that contribute to the food and nu-
trient sovereignty and security from direct and
indirect inventories (Table 1).
Table 1. Identification of orphan, obsolete, promisory and underutilized (forgotten) crops of Colombia.
Common
name Scientific name Family
Category Origin Classification Wild
parent Preservation
State (IUCN)* Orphan Obsolete Native PSPC Promi-
sing Under-
utilized Intro-
duced Dome-
sticated Semi-
dome-
sticated
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Almost threatened
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Minor worries
It continues in the next page
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
391
NUS according to the CFF
‘Crops for the Future’ (CFF 2015), the new
operative denomination for the ‘International
Centre for Underutilized Crops’ (ICUC) and the
‘Global Facilitation Unit for Underutilized Spe-cies’ (GFU) point out that NUS contribute to the
improvement of the survival means of human
populations since they:
1 Increase the farms income, valuing the life
style adopted by the family farming (AF);
2 Assure the food and nutrient sovereignty and security;
3 Encourage the creation of new markets,
mainly for eco-friendly produces;
4 Secure the production with low external
inputs and the stabilization of the ecosys-
tems;
5 Collaborate with increasing biodiversity,
because by supporting stress conditions,
they occupy important ecological niches,
Comes from the previous page
Common
name Scientific name Family
Category Origin Classification Wild
parent Preservation
State (IUCN)* Orphan Obsolete Native PSPC Promi-
sing Under-
utilized Intro-
duced Dome-
sticated Semi-
dome-
sticated Not evaluated yet
Not evaluated yet Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet Not evaluated yet Not evaluated yet Not evaluated yet Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet
Not evaluated yet Minor worry
Almost threatened
Not evaluated yet
Not evaluated yet
Not evaluated yet
Participatory breeding: tool for conservation of
neglected and underutilized crops
392
giving then support for functional redun-
dancy.
Participative breeding
The first projects involving the methodology of
participatory action research and more specifi-
cally the tool for participatory selection of plants tool (PSP), participatory breeding (PB) or
participatory plant breeding (PPB) in the late
1990s, were developed in Morocco, Syria and
Tunisia by ICARDA (International Center for
Agricultural Research in Dry Areas) (Cecarelli et al., 2001).
In these marginal areas, yield of staple
crops was low, while malnutrition and risk of
famine were high. Conventional breeding me-
thods were ineffective, centralized and in their
selection criteria did not include those features of importance for farmers (Walker, 2007).
Experience in Syria showed that decentra-
lized selection, associated with the participa-
tion of farmers from the beginning of the bree-
ding process resulted in the most appropriate
methodology to fit crops to specific biophysical, social and economic contexts, and thus re-
spond to the needs and knowledge of farmers
(Vernooy 2003, Vernoy and Song, 2004).
By Participatory Crop Improvement (PCI),
Participatory Plant Breeding (PPB), is under-stood a plant breeding strategy in which the
members of the productive chain (plant bree-
ders, technicians, farmers and others) work
together in the variety development process.
Opposite to the conventional plant breeding,
the PPB is decentralized and participative (Ce-carelli et al., 2001).
Therefore, linking communities is vital in
implementing a proposal of this nature, since
they are the ones who best know the origin,
behavior and adaptation of their seeds, in addi-
tion to direct contribution to food and nutri-tional sovereignty, through the promotion of
use of local resources for food and agriculture (Eyzaguirre et al., 1998).
The PB process is mainly characterized by
the systematized inclusion of the abilities, ex-
periences, practices, knowledge and expertise (Toledo Machado, Santilli and Magalhães,
2008), of the local communities in their reread
and perception of their environment. In this
way, the PB is a rescue and valuation tool for
the ancestral expertise and traditional knowledge associated to it.
The Participative Breeding reaches wider
objectives than the genetic ‘conventional’ or
‘formal’ breeding. According to Toledo Macha-do, Santilli and Magalhães (2008); Morris and
Bellon (2004), earnings in productivity are ob-
served together with, conservation and promo-
tion of biodiversity and genetic variability; gain
and use of adapted germplasm to local condi-tions; intrapopulational selection; evaluation or
participative selection of varieties; launch and
dissemination of new germplasm; diversifica-
tion of cropping systems and the production
and promotion of seeds. Being a decentralized
and participatory process contributes to the empowerment and decision making of key
managers and stakeholders: local populations.
For Almekinders and Elings (2001), the PB
is an alternative and complementary tool to the
conventional or formal plant breeding, which is closely related to the conservation in situ. The
main limitation of the formal breeding is based
on productivity or crop yield in favorable envi-
ronments with high use of chemical inputs and
irrigation; also does not consider cultural pre-
ferences and local conditions in marginal re-gions.
Among the methodologies, techniques and
tools used, work with traditional communities
developed today by the GIRFIN is oriented to-
ward methodologies of PR-Participatory Re-
search or PAR- Participatory Action Research. This has been applied in the study of the races
of maize described for Colombia, under the
approach of Participatory Breeding (PB), Parti-
cipatory Plant Breeding (PPB) or Participatory
Plant Selection (SPP).
Considered a strategy of conservation of
agricultural biodiversity, with the proposed
participatory plant breeding many of the cha-
racteristics of rusticity and adaptation of local
seeds remain. These seeds are the product of
selection pressure by traditional communities over time, driving the selection process accor-ding to their needs and preferences (Cecarelli et al., 2009). Therefore, the decision-making in a
PB program is complemented by the apprecia-
tion of farmers and agronomic results.
Among the preferences of communities, for maize, are the color of grains (yellow, white,
purple, red, black, etc.), type of grain (crysta-
lline, semi-crystalline and floury or soft), size
and grain shape; number of ears per plant, cob
size, number of rows on the cob; precocity; to-
lerance or resistance to pests or pathogens;
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
393
culinary use as cob and dry states, among
others.
According to Cecarelli (2012), from the two basic strategies for PB, in the PVS the goal is to
value the available germplasm. At the same
time, the PPB is applied with the goal of rescu-
ing and/or valuing the local varieties qualities
or, for marginal environments and/or crop conditions or strict quality specifications.
The PVS is easy to implement: its cost is
low and generates results at short term, it
means that the varieties are quickly adopted by
the farmers that participate in the process. On
the other hand, the PPB is useful to increase the genetic basis or, even when the implemen-
tation of PVS did not reach the successful re-
sults.
Under the perspective of Participatory
Breeding, in all the five stages of development of a new variety it is fundamental the participa-
tion of farmers, or community members. The
first three stages comprised the PPB. The first
four comprise the PVS:
1 Goals of selection (what characteristic is
aimed for selection);
2 Creation of variability (crosses);
3 Selection;
4 Evaluation;
5 Dissemination.
According to Machado et al. (2006), it is
essential that varieties, after rescued, be sub-jected to experimentation in different locations
and for several years to determine its value as a
local variety, allow their diffusion through the
exchange of materials by farmers, or assess
their potential for genetic breeding, validating its use in different agro-ecosystems. The evalu-
ation of different local maize varieties in diffe-
rent agro-ecosystems provides important gene-
tic sources for various types of biotic stress
(pests, diseases, weeds or companion planting)
or abiotic (Maize Program 1999).Additionally, through the PB the collection and assessment
of varieties adapted to local agro-ecological
conditions is given, which are associated with a
given functional agroecosystem. It should,
therefore, prioritize the development of varieties and their seeds, according to the requirements
of communities that can respond positively to
agro-ecological production systems.
Participative breeding of corn in farm and indigenous communities in
Colombia
In several Latin American countries, small far-
mers from the family farming have been in-
cluded in the rescue of the genetics of native
varieties and the preservation of the agro-
biodiversity in their farms, opposite to the cu-rrent model and the imposed global politics
(Santilli 2005, Santilli and Emperaire 2006).
For corn, experiences have been recorded in countries such as Brazil (Soares et al., 1998,
Machado et al., 2006), Honduras (Smith et al., 2001), Mexico (Smith et al., 2001; Zambrano,
2013) Argentina (Brocolli and Pardías, 2009), Guatemala (FAO 2011a, 2011b), among others.
In Colombia, the first proposal for PB in na-
tive corn “Recuperation and conservation of
native and indigenous corn from highlands in
Colombia under the methodology of participa-
tive breeding”, was developed by the GIRFIN between 2010-2011 (Vásquez and Caetano,
2011), in the surrounding of Tenerife-El Moral,
located on the western edge of the Central Cor-
dillera, municipality of El Cerrito, Department
of del Valle del Cauca. The local population is
In Colombia, the first proposal for PB in na-
tive corn “Recuperation and conservation of
native and indigenous corn from highlands in
Colombia under the methodology of participa-
tive breeding”, was developed by the GIRFIN
between 2010-2011 (Vásquez and Caetano, 2011), in the surrounding of Tenerife-El Moral,
located on the western edge of the Central Cor-
dillera, municipality of El Cerrito, Department
of del Valle del Cauca. The local population is
mainly originated in the Departments of An-tioquia (antioqueña, Colombian northwest) and
Nariño (nariñense, Colombian southwest). In
this zone abundant crops are long onion,
cilantro, cabbage, strawberry, blackberry,
among others. No large or medium corn crops
are found.
GIRFIN (Research Group on Neotropical
Plant Genetic Resources, Universidad Nacional
de Colombia - Palmira), that keeps a
germplasm collection of local races/varieties of
Colombian corn, supported by ICA, have se-lected initially the place for multiplication of
highlands corn seeds (those developed in ther-
mal floors above 1800 masl), in the Experi-
mental Station of the governorship of the De-
partment of Valle del Cauca in Tenerife, located
at 2664 masl, 3°43'47.8'' N and 76°4'35.6'' W
Participatory breeding: tool for conservation of
neglected and underutilized crops
394
and, El Moral at 2125 masl, 03°41'09.6'' N and
076°04'25.6'' W, with average temperature
between 10 °C and 17 °C and annual rainfall of 2.000 mm. The sowing happened in December
2009.
The diversity of corns awoke in the local
community interest in exchanging seeds, learn
methods of controlled pollination and new vari-eties for planting in their areas, although cha-
racterized as small areas (less than 1 ha), con-
sisting of solar, gardens or plots. Few families
have the right to possess the land. No corn
crops in medium or large scale and few local
varieties are planted, according to inventory by us.
The first socialization of the project at the
local school (Figure 1), was reported by local
radio, through brochures and personally. In
this, the corn characteristics required by far-mers were defined. Some farms select corn for
its production, that is, the number of ears per
plant, the size of cob, size and weight of grains,
or precocity, or grain colors or texture, or re-
sistance to cold and other abiotic and biotic
conditions.
It was agreed between the participants
(Tenerife and El Moral farmers, researchers
and technicians) that the experimental plot
(multiplication by GIRFIN) will be used for
workshops on the species biology and for con-
trolled pollination (Figure 1), but in each speci-
fic space each participant will give the manage-ment that he used to give to the crop.
Later, the experimental plot served as a
comparison with the farmers plots, where, the
traditional management benefits were easy to
document (crop associations, plantings accor-ding to the lunar calendar, among others), in
comparison to the conventional agricultural
management (chemical input use, monocrop
planting, breed germplasm).
Then, a socio-economical diagnose from
farm to farm was developed and the sowing area was established. In the second general
socialization the seeds of several races and va-
rieties (Capio, Pollo, Pira Naranja, ‘Timbrado’,
‘Porva’ –from savanna with floury grains– and
‘Arroz’ –from savanna with crystalline grains –) were delivered, that are supposedly adapted to
similar environmental conditions. Among the
local corns that were inventoried, corn seeds
exchanged were ‘Amarillo’, ‘Morocho’, ‘Negro’ de
Perú and Capio (‘Pintado’).
A practical workshop for recovery of tradi-tional uses of corn in feeding was done. In spe-
cial, the main forms for corn consumption were
shared (cob, wrapped, bread, corn bread, soup,
chicha, among others) in the event “First Mee-
ting Sharing the Harvest Nurturing Life – Cre-ole Corns" in the local school, September 24,
2011, with the aim of assessing the use of na-
tive seeds in food and promote the exchange of
traditional knowledge and seeds.
The community in Tenerife and El Moral do
not have a properly constituted association for defense of the conservation of local or intro-
duced and renatured genetic resources. Ho-
wever, among participants they highlighted
some arrangement for keepers of seeds, as they
keep on their farms an interesting biodiversity. These people can be identified as custodians or
guardians of seeds in Tenerife-El Moral, ie. with
conservationist calling (Figure 1).
The project achieved awareness of the im-
portance of conservation of native seeds, diver-
sity and traditional knowledge associated with the management of the maize crop. Germplasm
was identified with the greatest potential for
adaptation to agro-climatic conditions in the
region. In addition, other species of cold wea-ther such as quinoa (Chenopodium quinua), oca
(Oxalis tuberosa) and yellow potato (Solanum spp.) were recovered (Figure 2).
Figure 1. First socialization of the project in the village Tenerife, municipality
of El Cerrito, Valle del Cauca, Colombia. Jorge Isaacs School, 2010; a- b)
Socialization of the project: “Recovery of highlands corns” with members of
the community; c) Multiplication plot of highland corn in Sibundoy Valley,
Putumayo, Colombia; d) controlled pollination to obtain pure seeds. (Source:
GIRFIN, 2010-2012; photograph records with previous authorization).
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
395
Conceived to meet the needs of small far-
mers and their families in social conditions and economically marginal in different countries (Cecarelli et al., 2001), the PB was shown as an
efficient tool for contributing to food sovereign-
ty, conservation and use of plant genetic re-
sources in Tenerife, as it integrates the biologi-
cal component (knowledge and plant breeding) to the psychological and social dimensions of
human relationships (behaviors and cultures). Germplasm conservation on farms (in situ con-
servation ‘on farm’) and Participatory Breeding
resulted in innovative practices developed un-
der the PAR methodology (Participatory Action Research).
Finally, the extension of the proposal was
requested by indigenous communities Koko-
nuko (Cauca) and Camentsá Biya (Putumayo),
in July 2011, which led to develop the project
in the framework of the First National Call for Solidarity Extension – Direction for National
Extension of the Universidad Nacional de Co-
lombia.
Towards the creation of a PB program
The area of influence of the Universidad
Nacional de Colombia - Palmira reaches all the
southwest of the country (Putumayo, Nariño,
Cauca and Valle del Cauca), which receives
indigenous and rural students of the highlands and lowlands, whose benefit from research and
extension with regional agricultural vocations,
complementing their practical-empirical– tradi-
tional knowledge.
The goal of a new phase of the project PB
was to contribute to the conservation and re-
covery of Colombian races of maize, also strengthening the food sovereignty of indige-
nous communities of Kokonuko in Puracé
(Cauca) and Camentsá in the Sibundoy Valley
(Putumayo) and farmers of Santa Teresa-La
Quisquina (Palmira) and Tenerife-El Moral (El Cerrito, Valle del Cauca), through the reap-
praisal of traditional knowledge associated with
the use and crop management.
The socialization of the proposal with co-
mmunities was followed by a diagnosis of par-
ticipating families by semi-structured inter-views, participant observation and indirect ob-
servation (literature review) on the study areas.
Later, training workshops were conducted in
techniques for controlled pollination and data
acquisition for characterization according to the interests of communities.
In areas of indigenous reserves the recogni-
tion and documentation in the field of local
varieties and traditional management was also
performed, being two populations culturally
entrenched to corn and preservers of an exten-sive knowledge of the species. For Santa Tere-
sa-La Quisquina was conducted in parallel an
inventory of plant diversity on farms.
From the upland germplasm multiplied un-
der controlled pollination samples were stored in the working collection of GIRFIN and also,
seeds for donation were arranged for the partic-
ipating communities and new exchanges.
‘Highlands’, 'high' or 'cold lands' corns are
those races (or varieties) that develop from
1800 masl therefore are adapted to cold wea-ther and, usually present annual development.
Roberts et al. (1957), have recognized for
Colombia 23 corn races, 12 are from highlands
and 11 from lowlands (between 0 and 1800
masl). Highlands races are: Pira, Pollo, Imbri-
cado, Pira Naranja, Maíz Dulce, Cabuya, Mon-taña, Amagaceño, Capio, Sabanero, Clavo and
Harinoso Dentado. Additionally to the de-
scribed races, GIRFIN preserves in its collection
locally identified germplasm, from different
regions of the country which is called native corn or native variety (Figure 4). It is the case of
‘Rojo’, ‘Negro’, ‘Amarillo’ (Putumayo), ‘Granizo’,
‘Granizado’ (Putumayo, Nariño), ‘Diente de Ca-
ballo’, ‘Propio’ (Cauca), among others.
The communities linked to the PB process
(Figure 3) have the following general charac-teristics:
Figure 2. Corn varieties adapted and multiplied by farmers of the village
Tenerife, Cerrito, Valle del Cauca in 2011; a) Corn Pollo; b) Negro Peruano,
Timbrado and Amarillo (izq.-der.) Promotion of other species of feeding
importance in moderate cold weather; c) Fava bean (Vicia faba); d) V. faba
associated with oca (Oxalis tuberosa); e) Quinoa (Chenopodium quinoa); f)
potato seeds (Solanum phureja). (Sources: Nunes Pazdiora B.R.C., GIRFIN,
2010-2013; Vásquez D.L., 2011).
Participatory breeding: tool for conservation of
neglected and underutilized crops
396
1 Rural community village of Santa Teresa,
municipality of La Quisquina, Palmira, Va-
lle del Cauca. Located in the foothills of the Central Cordillera between 1600 and 1900
masl, with a climate of tropical dry forest.
The study area is located between 1,745
masl 3°35'50,50'' N and 76°10'12,94'' W
and 1673 masl 3°35'46.6'' N and 76°10'7,50'' W. Average temperature of 20
°C. Annual average rainfall of 1010 mm.
Composed of eight families from different
regions of the country who migrated to this
area for nearly five years ago, after being
displaced from their own territories.
2 Rural community of the village of Tenerife,
El Cerrito, Valle del Cauca. Located in the
western mountain range with fog forest
ecosystem is part of the buffer zone of the
National Natural Park Páramo de las Hermosas, with temperature between 10 °C
and 17 °C. Annual rainfall of 2000 mm. The
area in which this proposal was developed
is at an altitude between 2664 masl
3°43'47.8'' N and 76°4'35.6'' W and 2125 masl 3°41'09.6'' N and 76° 04'25.6'' W.
Group composed of five families in the area.
3 Indigenous community Kokonuko, reserva-
tion of Purace, Cauca, at 2818 masl
2°22'39,27'' N and 76°27'10,09'' W. Tempe-
rature between 10° and 17 °C. Annual ave-rage rainfall 1811 mm. Group of seed
keepers of the Cabildo Purace, villages
Chapio, Ambiro, el Tablon and Carpinteria.
Group composed of ten keepers (10 fami-
lies). This indigenous group is located in the central-eastern department of Cauca, in
the municipality of Purace, on the western
slope of the Central Cordillera area. Its te-
rritory is located on the right bank of the
upper basin of the Cauca River; in a range
of altitude between 2400 and 4000 masl.
4 Indigenous community Camëntsa Biyá in
Sibundoy, village San Felix, Sibundoy, Pu-
tumayo. Located in southwestern Colombia
in the foothills of the Colombian Macizo in
the Andes-Amazon region, northwest of the department of Putumayo at an altitude of
2200 masl, 1°10'50,75'' N, 76°53'05,47'' W.
With an average temperature of 16 °C.
Annual average rainfall of 2300 mm. Group
composed of 10 elders of the community
group.
Throughout the entire process of PB the
use of native corn for feeding was promoted
through practical workshops for recovery of
traditional food uses of corn. On each day or
encounter different traditional recipes from each region were prepared with corns from the
same communities, involving the whole family.
Considering the lack of a generational
change in rural areas of Colombia, participa-
tion is encouraged in children of families in
integration activities and assessment of daily tasks that preserve landraces. Seed and
knowledge exchanges among participating fa-
milies and GIRFIN and dissemination tech-niques for ex situ conservation of seeds were
other key activities in the process of awareness
of the importance of traditional knowledge.
Figure 3. Communities linked with the stage II: Participatory breeding in
traditional communities of Colombia: a) Rural community village Santa
Teresa, La Quisquina, Palmira, Valle del Cauca; b) Rural community of the
village Tenerife, El Cerrito, Valle del Cauca; c) Indigenous community
Kokonuko, reserve Puracé, Cauca; d) Indigenous community Camëntsa Biyá
in Sibundoy, village San Felix, Sibundoy, Putumayo. (Sources: GIRFIN, 2011-
2012; Vásquez D.L., 2012; photograph records with previous authorization).
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
397
The adoption of the strategy PPB is due to
that in the worked areas, which are introduced
in the Andean region or Andean foothills, much of the production of basic grains, roots and
tubers, it is carried out in marginal conditions
by small and medium producers. These far-
mers make almost no use of improved varieties,
believing that these do not respond well in marginal conditions and/or low input systems.
They also consider that improved varieties
are not always adapted to the different uses
given to a local variety, and that access to im-
proved seeds is limited, it has a high cost
(technology package). Therefore, in these tradi-tional agro-ecosystems predominate informal
seed systems, with swaps and exchanges.
Through the PPB local genetic diversity at
risk and underutilized is promoted, valued and
the ancestral knowledge, preferences of far-mers, agro-ecological conditions and cultural
practices are considered and finally, there is
better control of genotype x environment inte-ractions (Soares et al. 1998). It is also possible
to do a gender analysis, which determines who
participate in the various decisions and there-fore the impact of such participation in re-
search. This tool is understood as a particular
type for stakeholder analysis, where the most
important variable to discriminate the defini-
tion of the interest group is the genus (CGIAR 1999, Lilja et al. 2001).
As stated by Desclaux (2005) and Toledo
Machado, Santilli and Magalhães (2008), the
right of the farmers and/or holders of agricul-
tural biodiversity as cultural heritage collective-
ly built as local varieties, practices, accumula-
ted ancestral knowledge and innovation, which together constitute the traditional knowledge
must be guaranteed by legal instruments. Al-
though indigenous and rural communities play
an important conservationist role, they are ex-
cluded from political processes and decision making. Inadequate policies and laws related to
the PGR can be major causes of genetic ero-
sion, because they recommend sowing high-
yielding varieties, a process that leads to the
replacement of varieties, traditional practices
and uses.
Germplasm selection
In the study described here for some communi-
ties PVS was adapted and for others PPB was
used. Thus, for Tenerife the available Capio
corn germplasm was valued. For Purace and
Sibundoy communities the local varieties were
valued such as Yucatan and Capio for the first one and ‘Granizo’, ‘Timbrado’, ‘Rojo’ and ‘Negro’
for the second one. In corn the genetic variabi-
lity is high, reducing the stage for creation of it.
As methodologic tools surveys were used with a
semi-structured questionnaire, participant ob-servation, theory-practical workshops, seed
fairs and interchange of knowledge (thought
meetings).
Stages developed
1 Local germplasm rescue: it was done with
the aim of increasing the genetic variability
of the corn varieties in the village San Felix,
in the municipality Sibundoy, to select vari-
eties better adapted to this agro-ecosystem.
Besides local varieties, varieties or races from other locations in Colombia were tes-
ted to know their behavior under the
weather conditions of the Sibundoy Valley.
2 Evaluation assays: in order to know the
genetic variability of the rescued varieties, evaluating their adaptation to the local en-
vironment and the system of agro-ecological
production, exchange experiences of far-
mers in different communities, workshops
in the field for learning assisted pollination
and genetic diversity of corn, two trials were conducted, the first in the San Felix, in Si-
bundoy, Putumayo and the second in La
Quisquina, Palmira, Valle del Cauca.
The trial established in Sibundoy aimed to
increase and characterize the morpho-
agronomy of highland materials from the GIRFIN collection (70 entries). In this collec-
tion are included 14 entries from the mu-
nicipalities Sibundoy, Santiago and San
Francisco. In the case of the materials tes-
ted in La Quisquina, the aim was to in-crease and observe the behavior of some
materials in these weather conditions, at
1800 masl, since some varieties considered
lowland and upland were planted there.
From the morphoagronomic characteristics
evaluated for selection were considered: (1) days to male flowering; (2) days to silking;
(3) plant height (m); (4) ear height (m); (5)
length of the cob; (7-9) average, basal and
apical diameter of the ear; (10) number of
rows from the cob; (11-13) color, type and texture of the grain; (14-15) length and
Participatory breeding: tool for conservation of
neglected and underutilized crops
398
number of branches of the spike, among
others, similarly to Machado (1998), in a
program of PPB with local maize varieties in Brazil.
3 Stratified massal selection in corn crops:
methodology of plant breeding to select in-
dividuals by the phenotype, to improve
agronomical characteristics of interest for the user. Involves five steps at different
growth stages of the plant (Witcombe and
Virk 2009). These are:
3.1 Pre-sowing (seed selection) and sowing
(plot location, sowing, isolation);
3.2 Vegetative (identification of the plot, di-vision of the plot, plant labelling, and
labelling and selection of plants);
3.3 Reproductive (removal of male flowers
in undesirable plants, selection and la-
belling of plants);
3.4 Physiological maturity (selection by co-
verage, harvesting) and
3.5 Pre and post-harvesting (drying, sto-
ring).
In the present study the selection of the
features of interest to farmers initially was the agroclimatological adaptation; all harvested
material was planted in the next cycle to in-
crease the adaptation and amount of seeds.
It is recognized by several participants that
expectations towards the material selected ini-tially for planting do not necessarily resulted in
a good harvest, for example floury materials
have a high rate of rotting in fresh cob, which
prevented obtaining seed. Despite this, the
Capio corn from Sibundoy, with floury texture,
showed their adaptation to a stable production with grain quality considered by the farmer as
"excellent”.
Promoting use of local breeds and varieties
with their food and nutraceutical qualities or
generates in every local community and the tendency to increase, improve and maintain the
culture thereof. Participation in the practice of
food processing by individual family members,
using own resources, is a way of revaluing cul-
tural traditions, recreating them according to
the needs of new generations (De la Calle, 2010).
For this reason, intrinsic to plant research,
is fundamental the integration to wider pro-
grams that allow continuity for the search of
local varieties that are more stable, the improve
the life quality of farmers in their regions and
strengthen their culture and identity, which is very important to preserve the knowledge of the
native communities.
Production of community seeds
The seed production work was always linked to Participatory Breeding works. Within the care
measurements adopted by communities are the
choice of area and isolation of the field to avoid
contamination. Storage was done in plastic
bottles or traditional systems being the most widely used the conservation of whole cobs to
constant smoke from wood stove.
The genetic variability of corn is a strength
for the Department of Putumayo and south-
western Colombia, as it represents a significant
reservoir of different kinds of this grain that strengthen the sovereignty and food and nutri-
tion security. Corn is tied to social, cultural
and historical processes of traditional commu-
nities, being considered a cultural and natural
heritage (Zambrano 2013, Caetano and Díaz 2014).
In addition to contributing with the conser-
vation and sustainable management of the pre-
sent genetic variability of corn, rescue and va-
luing traditional knowledge, empowerment of
stakeholders with knowledge about how to ac-quire their own breeding varieties according to
their own selection objectives was emphasized. According to Machado et al. (2006), empower-
ment (or self-independence efforts in communi-
ty development) of rural communities can be
made from the sustainable management of ag-ricultural biodiversity in agro-ecological sys-
tems.
The loss of farming systems, races and local
varieties cause that the values (ie. cultural and
social) are also lost, as a result of erosion pro-cesses impoverishment of communities of sub-
sistence farmers is verified, which puts at risk
the security and food and nutrition sovereignty (Stella et al. 2006).
How much of the diversity of races have
been really lost? How much of these have been transformed into modern varieties? How much
diversity was collected by previous explorers?
and how much it is preserved in genebanks?
Are the races conserved enough for agriculture
today and tomorrow? These are the questions to be resolved, according Hammer et al. (1996).
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
399
The development of this proposal for PB in
southwestern Colombia allowed, for some
communities, restitution of the diversity of na-tive and indigenous corn and contributed to the
use, management and conservation of local
varieties of high value of direct and indirect
use, or value of nonuse - option, heritage and
existence. PB program has to be innovative regarding food security policies without propo-
sing transitional and short-term measures but
structural transformations, for social inclusion
and income generation to needy families. In
addition to food security, it should prioritize
strengthening family agriculture (production for own consumption), since it can be produced in
sufficient quantities, nutritional quality and
facilitate access to feed the local population in
a situation of social vulnerability and food in-
security (Gazzolla and Schneider, 2004).
However, as a turning point, Desclaux
(2005) notes that the PPB should not be re-
duced as 'assisted selection by the farmer'.
Agronomists are support for farmers in a better
characterization of the environment. As crop-
ping systems are associated to social criteria, their identification leads to recognize the real
needs of farmers, and therefore generate more
suitable varieties. The PPB should not be lim-
ited to studies for a limited time to document
indigenous knowledge and preferences period farmers.
For efficiency, the participation should be a
permanent characteristic of the plant breeding
programs associated to crops in difficult agri-
culture and surroundings with the environ-
ment (Desclaux, 2005). According to Morris and Bellon (2004), “more participation is not
necessarily better. Participation should be seen
as a mean towards an aim”.
The main goals of the PB are to get a locally
adapted germplasm, promote the genetic diver-sity and viable the empowering in the farmers.
It is not a program lead by farmers, neither by
a formal professional organization. The interac-
tion is collegial and decentralized, with farmer
participation during the first three steps of the
breeding scheme. Participating farmers have the right to be considered partners of the
breeding program and not just consumers or
end users varieties (Desclaux, 2005).
New corn races for Colombia: PGR for value and use
During the 50’s a process for collection of na-
tive and indigenous corn was done in most of
the Colombian territory, recording 1899 entries for the national germplasm bank. One of the
products was the description and classification
of all the germplasm in 23 races, grouped into three racial groups (Roberts et al., 1957). The
first group, Primitive races, is composed for
only two races. The second group, with nine races, is known as Probably Introduced. Fina-
lly, the third group, de Colombian Hybrids
comprises 12 races (Table 2).
Between the years 2007-2014 the GIRFIN,
supported by the Colombian Agricultural Insti-tute (ICA), made a sampling in those places described by Roberts et al. (1957) comparing
the ecogeographical distribution in these two
times (50’s and now). Thus, we increase to 34
the number of races of Colombian corn and
described an important number of local varie-ties (Figures 4 and 5, Caetano et al., 2014).
All this germplasm of corn is considered
with the NUS criteria. Additionally, we postu-
late a fourth racial group and the existence of a
genic complex formed by the variants of the
race Chococeño. Therefore, the racial groups according to Caetano et al. are: Primitive, In-
troduced Colombian Hybrids and Strictu Sensu
Colombian Hybrids Races (Table 2).
The morphological analysis (Maigual and
Caetano, in preparation) and the molecular
analysis done (RAM, SSR and cpDNA, genomic region AtpB-1-RbcL-1; Revelo et al., 2015) iden-
tified three racial groups defined by Roberts et al. (1957), although with variation among the
races that composed them and, a fourth group.
The cpDNA study located the race Imbricado in
the ‘Primitive’ racial group together with Pollo
and Pira, all pop-up corn of small cobs and crystalline grains (Table 2).
With cpDNA, for the ‘(Probably) Introduced’
group were determined seven of the nine races described by Roberts et al. (1957). Both catego-
ries have in common the races Güirua, Clavo,
Andaquí and Cariaco. To the seven races are associated Yucatán, Costeño and Cabuya. Ad-
ditionally, with the recently introduced races
are 13 races: Güirua, Clavo, Andaquí, Cariaco,
Yucatán, Costeño, Cabuya, Morocho, Moro-
chillo, Capia, Negro Peruano, Canguil and
Participatory breeding: tool for conservation of
neglected and underutilized crops
400
Chulpi or ‘Ecuadorian Sweetcorn’ (Caetano et al., 2014).
The third racial group ‘Colombian Hybrids’
is composed of 13 races according to the cpDNA analysis (Revelo et al. 2015), with simi-
lar races counting for nine in relation to Ro-berts et al. (1957). These two categories do not
share the races Pira Naranja, Sabanero,
Harinoso Dentado and Maíz Dulce, since Ro-berts et al. (1957) considered them as ‘Probably
Introduced’. The other races, common to both studies are Montaña, Negrito, Puya, Cho-
coceño, Amagaceño, Común, Puya Grande,
Capio and Cacao.
Based on the studies developed by us, the
‘Colombian Hybrid’ races are: Montaña, Negri-
to, Puya, Puya Grande, Amagaceño, Común,
Pira Naranja, Sabanero, Harinoso Dentado,
Chococeño complex (with its variants), plus the new races Caucano, Timbrado, Azul Vallecau-
cano, Negro de Tabanok and Rojo Sureño, for a total of 15 races (Caetano et al. 2014).
Based on the cpDNA, the Colombian
Sweetcorn comprises, together wih Capio and
Cacao, a group derived from the Colombian Hybrids. This two latest races are categorized both, by Roberts et al. (1957) and by the
cpDNA, as Colombian Hybrids. Possibly the
Colombian Sweetcorn and Capio are influenced
by Ecuadorian germplasm of ‘Sweet corn or
Chulpi’ and from ‘Capia’ respectively. Cacao is related by its floury endosperm and aleuronic
color, also present in Capio. This group is
Table 2. Distribution of racial groups of Colombian corns according to
Roberts et al. (1957) and Caetano et al.
Colombian corn races
Racial group
Primitives
Probably
introduced
Colombian Hybrids
Strictu sensu Colombian
Hybrids
Figure 4. Colombian races and varieties of corn. (Source: Vásquez D.L., 2011).
Figure 5. A show of corn variability in Colombia. a) Amarillo Corn; b)
Timbrado Corn; c) Negro Corn; d) Rojo Corn. (Source: Caetano Nuñes D.,
GIRFIN, 2013).
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
401
named ‘Strictu sensu Colombian Hybrids’ (Cae-tano et al. 2014), because of their germplasm
origin (Table 2).
Perspectives
The native and indigenous seeds are a heritage
and invaluable genetic reservoir and are the
basis for improving local seed systems and corn production. Therefore, the Community reserves
of seeds should be considered a local technolo-
gy alternative to support climate change mitiga-
tion in vulnerable communities and revive pro-
duction, therefore there is a need to assess the
feasibility of an additional study to address this issue from the social point of view.
The PB is a research validated tool that
guides and defines the process of obtaining
plant varieties, in accordance with the prefer-
ences and needs of farmers and their environ-ment. Graphic documentation may be a greater
impact, since besides the self-recognition of the
participants in these outreach materials serve
as input for the awareness of children for con-
servation. Moreover, recognition of local au-
thorities is necessary and that regional and/or national government directives consider the
establishment of permanent PB programs with
communities.
In the present study, it is observed that
farming aimed at family food production in traditional communities are now almost exclu-
sively in the hands of the elderly. The need to
involve young people in order to maintain tradi-
tional knowledge associated, conserve native
seeds and bring them to their environment is
evident. The above is a strategy to be used by the directives to generate empowerment of the
possibilities offered in the environment, so that
they are directly involved in its territory and
reduce the migration to urban centers.
The methodology PPB provided along germplasm adapted and improved to local
needs of communities, empowering partici-
pants’ knowledge, strengthening communities
in their cultural identity and the integration of
isolated communities with different entities of
the civil society (academic institutions, scien-tific, local authorities). Therefore, it should be
inserted in the academic context of the relevant
areas, in addition to continuing education pro-
grams.
According to Machado et al. (2008), institu-
tions and government entities should encou-
rage the development of participatory research,
including MP, to strengthen family farming and
public policies directed at the conservation and sustainable use of agricultural biodiversity, in
order to adopt a sustainable model of produc-
tion to respond effectively to security and food
and nutrition sovereignty of local populations.
We complement that universities, through their mission of solidary extension, should encou-
rage the dissemination of this tool, training
professionals from a more holistic view.
It is highly feasible an integrated conserva-
tion and utilization of PGRFA approach. Such
approach should be anchored on increasing productivity through continued access and
exchange of genetic resources; sustainability
resulting from the combination use-
preservation; the partition of the benefits re-
sulting from the use of PGR and equity through the full participation of those responsible for
the conservation of these resources.
Acknowledgements
To the DNIE – National Direction of Research and Extension, Solidarity Extension Office of
the UNAL for the financial support and the
great quality technical assistance to the Project
of Solidarity Extension ‘Native Corns’, National
call 2012.
To the Indigenous Cabildo Camëntsa Byiá in the Sibundoy Valley, Putumayo, Colombia.
To the communities and people that su-
pported us, and with who we share these
achievements.
References
Anderson, E., and Cutler, H. C. (1942). Races of Zea mays: I. Their recognition and classification . Annals of the Missouri Botanical Garden, 29, 69-88. Retrieved from http://www.biodiversitylibra ry.org/item/54271#page/77/mode/1up
Bohrer Monteiro, M. V., and Veasey, E. A. (2009). Raíces y tubérculos tropicales olvidados o subutilizados en Brasil. Revista Colombiana de Ciencias Hortícolas, 3(1), 110 - 125. Retrieved from http://revistas.uptc.edu.co/revistas/index. php/ciencias_horticolas/article/view/1203/1202
Broccoli , A., & Pardías , S. (2009). El rescate de semillas como aporte a la soberanía alimentaria. Descripción de una experiencia de conservación de maíz con agricultores familiares santafecinos., (pág. 19). Buenos Aires, Argentina.
Caetano, C. M., and Díaz, J. A. (2014). Evaluación
del grado de variación genética en las razas de
Participatory breeding: tool for conservation of
neglected and underutilized crops
402
maíz criollo e indígena de Colombia. UNAL-GIRFIN; UNAL-ICA.
Caetano, C. M., and Vásquez D, L. N. (2011). Recuperación y conservación de maíces criollos e indígenas de altura de Colombia bajo la metodología de mejoramiento participativo. VIII
Simposio Internacional de Recursos Genéticos de América Latina y El Caribe. Quito, Ecuador: SIRGEALC. Retrieved from http://es.scribd. com/doc/203782436/SIRGEALC-2011-
Resumenes#scribd Cecarelli , S., Grando, S., and Capettini , F. (2001).
La participación de los agricultores en el mejoramiento de la cebada en el ICARDA. En L. Daniel, Memorias de la Conferencia Internacional
sobre futuras estrategias para implementar mejoramiento participativo en los cultivos de las zonas altas de la región Andina (págs. 23 - 27).
Quito, Ecuador. Ceccarelli, S. (2012). Plant breeding with farmers - a
technical manual. Aleppo, Syria: ICARDA. Retrieved from https://www.researchgate.net/ publication/236962212_Plant_Breeding_with_Farmers__a_Technical_Manual_ICARDA_Aleppo_Syria
Ceccarelli, S., Grando, S., Singh, M., MIchael, A., Shikho, M., Al Issa, A., . . . Al Hasan, A. L. (2003). A methodological study of participatory barley breeding. II. Response to selection. Euphytica,
185 - 200. doi:10.1023/A:1025535609828 Ceccarelli, S., Guimarães, E. P., & Weltzien, E.
(2009). Plant breeding and farmer participation. Rome, Italy: ICRISAT, ICARDA, FAO. Retrieved from ftp://ftp.fao.org/docrep/fao/012/i1070e/ i1070e.pdf
Consultive Group on International Agricultural Research (CGIAR). (1999). Crossing perspectives:
farmers and scientists in participatory plant breeding. Cali, Colombia. 49 p. Retrieved from http://ciat-library.ciat.cgiar.org/articulos_ciat/crossing.pdf
De la Calle, R. (2010). Gastrobotánica: 100 temas al natural para cada estación de año. Madrid, España: Temas de Hoy. 216 p.
Dudley, N., Buyck, C., Furuta, N., Pedrot, C., Renaud, F., and Sudmeier-Rieux, K. (2015).
Protected Areas as Tools for Disaster Risk Reduction. A handbook for practitioners. Tokyo and Gland, Switzerland: MOEJ and IUCN. doi:10.2305/IUCN.CH.2015.02.en
Espinosa, P., Vaca, R., Abad, J., and Crissman , C. C. (1996). Raíces y tubérculos andinos. Cultivos
marginados en Ecuador. Situación actual y limitaciones para la producción. Quito, Ecuador: Departamento de Ciencias Sociales del Centro Internacional de la Papa, Estación Quito. Ediciones Abya-Yala. 178 p.
Eyzaguirre, P. B., Padulosi, S., and Hodgkin , T. (1999). IPGRI's strategy for neglected and underutilized species and the human dimension of agrobiodiversity. In S. Padulosi, Priority-setting
for underutilized and neglected plant species of the mediterranean region (págs. 1-19). Rome, Italy:
International Plant Genetic Resources Institute (IPGRI).
FAO. (2011). Agricultores mejoradores de su propia
semilla. Fortalecimiento de la producción de maíz a través del mejoramiento participativo en comunidades de Sololá. Sololá, Guatemala. 56 p. Retrieved from http://www.fao.org/3/a-ar65 3s.pdf
FAO. (2012). Manual técnico de fitomejoramiento
participativo de maíz en áreas de altiplano y de sequía en Guatemala. Ciudad de Guatemala, Guatemala. 44 p. Retrieved from https://coin. fao.org/coin- static/cms/media/11/1330537297 5590/manual_fitomejoramiento_participativo_nov _ 2012_atinar_ii.pdf
FAO. (2014). State of Food and Agriculture.
Innovation in family farming. Economic and Social Development Department. Rome, Italy. 175 p.
Retrieved from http://www.fao.org/3/a-i4040e .pdf
Hammer, k., Knüpffer , H., Xhuveli , L., and Perrino, P. (1996). Estimating genetic erosion in landraces - two case studies. Genetic resources and crop evolution, 43(4), 329- 336. Retrieved from http://link.springer.com/article/10.1007/BF00132952
Hernández Bermejo, J. E., and León, J. (1992).
Cultivos marginados : otra perspectiva de 1492. Roma, Italia: FAO. Produccion y proteccion vegetal, 339 p.
Hernández-Bermejo, J. E. (2013). Cultivos infrautilizados en España: pasado, presente y futuro. Ambienta, 38 - 55. Retrieved from http://www.revistaambienta.es/WebAmbienta/marm/Dinamicas/pdfs/versionpdf/Esteban13.pdf
La vía campesina. Movimiento campesino internacional. (2003). ¿Qué significa soberanía alimentaria? Retrieved from http://www.redes. org.uy/wp-content/uploads/2008/09/que-signifi ca-soberania-alimentaria.pdf
Machado, A. T. (1998). Resgate e caracterização de variedades locais de milho. In: Soares AC, Machado AT, Silva BM, von der Weid J.M. eds. Milho Crioulo: conservação e uso da biodiversidade. Rio de Janeiro: AS-PTA.
Manrique, K. (2000). Nociones de manejo
postcosecha. Documentos Centro Internacional de la Papa. Lima, Perú: Ministerio de Agricultura del Perú.
Morris, M., and Bellon, M. (2004). Participatory plant
breeding research: Opportunities and challenges for the international crop improvement system. Euphytica, 136(1), 21 - 35. doi:10.1023/B:EUPH. 0000019509.37769.b1
Naciones Unidas. (1992). Convenio sobre la diversidad biológica. Río de Janeiro, Brazil.18p. Retrieved from https://www.cbd.int/doc/legal/cbd-es.pdf
Padulosi, S., and Hoeschle-Zeledon, I. (2004). ¿A qué denominamos especies subutilizadas? Leisa. Revista de Agroecología, 20(1), 6- 8. Retrieved from http://www.leisa-al.org/web/images/sto
ries/revistapdf/vol20n1.pdf
Acta Agronómica. 2015. 64 (3) Supplement, p 383--403
403
Pardo de Santayana, M., Morales, R., Aceituno, L., Molina, M., and Tardío, J. (2012). Etnobiología y biodiversidad: el inventario español de los conocimientos tradicionales. Ambienta, 99, 6 -25. Retrieved from http://www.revistaambienta.es/ WebAmbienta/marm/Dinamicas/pdfs/versionpdf/Tradicional.pdf
Pastor, S., Fuentealba, B., and Ruiz, M. (2007).
Cultivos subutilizados en el Perú. Análisis de las Políticas Públicas Relativas a su Conservación y Uso Sostenible. Fiumicino, Italia: The Global Facilitation Unit for Underutilised Species (GFU);
Asociación Civil Pro Uso DIVERSITAS - PROUD; Sociedad Peruana de Derecho Ambiental – SPDA . Retrieved from http://www.spda.org.pe/?wp fb_dl=62
Programa de Maíz. (1999). Desarrollo, mantenimiento
y multiplicación de semilla de variedades de polinización libre. Mexico D.F.: CIMMYT. 16 p. Retrieved from http://repository.cimmyt.org/ xmlui/bitstream/handle/10883/762/68195.pdf
Revelo Portilla, E. A., Cardozo Conde, C. I., and Caetano, C. M. (2015). Estudio molecular preliminar de accesiones de maíz (Zea mays L.) criollo e indígena colombiano utilizando una región de ADN cloroplástico. Acta Agronómica, 64(1), 72 - 82. doi:10.15446/acag.v64n1.40724
Roberts, L., Grant, U. J., Ramírez, R. E., Hatheway, W. H., Smith, D. L., and Mangelsdorf , P. C.
(1957). Razas de maíz en Colombia. D.I.A. Boletín Técnico No.2. Bogotá, Colombia: Ministerio de Agricultura. Editorial Máxima. 159 p.
Silva Ramos, M. Á. (2002). El rol de los cultivos marginales en la seguridad alimentaria. La Paz, Bolivia: Instituto Interamericano de Cooperación para la Agricultura.Oficina IICA Bolivia.
Smith, M. E., Castillo, F. G., and Gómez, F. (2001). Participatory plant breeding with maize in Mexico and Honduras. Euphytica, 122(3), 551 - 563. Retrieved from http://link.springer.com/article/ 10.1023/A%3A1017510529440
Soares, A. C., Machado, A. T., Silva, B. M., & Von Der Weid, J. M. (1998). Milho Crioulo: Conservação e uso da biodiversidade. Rio de
Janeiro, Brazil: AS-PTA.185 p. Thies, E. (2000). Promising and underutilized species
crops and breed. Eschborn, Germany: GTZ. 23 p. Obtenido de https://cgspace.cgiar.org/bit stream/handle/10568/3682/thies.pdf?sequence=1
Toledo- Machado, A., Arcanjo- Nunez, J., Torres, d. C., Lourenço-Nass, L., and Rocha Bettero, F. C.-d. (2006). Mejoramiento participativo en maíz: su contribución en el empoderamiento comunitario en el municipio de Muqui,Brasil. Agronomía mesoaméricana, 17(3), 393 - 405. Retrieved from
http://www.mag.go.cr/rev_meso/v17n03_393.pdf
Toledo Machado, A., Santilli, J., and Magalhães, R. (2008). A agrobiodiversidade com enfoque agroecológico : implicações conceituais. Brasília, DF: Embrapa Informação Tecnológica. (Texto para Discussão / Embrapa. Secretaria de Gestão. Retrieved from https://www.embrapa.br/docu ments/1035106/1047819/texto34.pdf/5448d115-890d-4314-b7ff-ba46b9687671
Toledo Machado, A., Torres de Toledo, C., and Lourenço Nass, L. (2011). Manejo da diversidade
genética e melhoramento participativo de milho em sistemas agroecológicos. Revista Brasileira de Agroecologia, 6(1), 127 - 136. Retrieved from http://www.abaagroecologia.org.br/revistas/index.php/rbagroecologia/issue/view/52
UPOV. (1991). Convenio Internacional para la Protección de las Obtenciones Vegetales. Ginebra, Switzerland. Retrieved from http://www.upov. int/portal/index.html.es
Vernooy, R. (2003). Semillas generosas. Mejoramiento participativo de plantas. Ottawa, canadá: IDRC- CRDI . Retrieved from https://idl-bnc.idrc.ca/ dspace/bitstream/10625/52959/1/IDL-52959. pdf
Vernooy, R., and Song, Y. (2004). New approaches to
supporting the agricultural biodiversity important for sustainable rural livelihoods. International Journal of Agricultural Sustainability, 2(1), 55 - 66. Retrieved from http://betuco.be/voor lichting/New%20Approaches%20to%20Supporting%20the%20Agricultural%20Biodiversity.pdf
Walker, T. S. (2007). Participatory Varietal Selection,
Participatory Plant Breeding, and Varietal Change. Washington, DC. USA: Background paper for the World Development Report. Retrieved from http://hdl.handle.net/10986/9182
Witcombe, J. R., and Virk, D. S. (2009). Methodologies for generating variability. Part 2: Selection of parents and crossing strategies. In S. Ceccarelli, E. P. Guimaraes, & E. Weltzien. Rome, Italy: Plant Breeding and Farmer Participation. FAO.
WCMC. World Conservation Monitoring Centre. (1992). Global Biodiversity: Status of the Earth’s
Living Resources. London, UK: Brian Groombridge.
Zambrano Zambrano, E. E. (2013). Valoración del
mejoramiento genético participativo in situ en poblaciones de maíz (Zea mays L.) criollo en el sureste del Estado de México. Montecillo, Texcoco, Mexico: Master thesis on Science, Genetics. Postgraduate School. Retrieved from http://hdl. handle.net/10521/1863.